| Literature DB >> 35729207 |
Annalisa Romani1, Giulia Marrone2, Roberto Celotto3, Margherita Campo1, Chiara Vita4, Carlo Chiaramonte5, Andrea Carretta6, Nicola Di Daniele7, Annalisa Noce8.
Abstract
Several studies highlighted a correlation between exhaled air volatile organic compounds (VOCs) and some pathological conditions, such as chronic kidney disease (CKD), chronic liver disease, etc. In fact, in literature has been reported that CKD is characterized by an increased concentration of ammonia, trimethylamine (TMA) and isoprene compared to healthy subjects. Currently, there is not a validate and standardized method to detect VOCs. For this purpose, we examined the utility of selected ion flow tube-mass spectrometry (SIFT-MS) to measure VOCs in CKD patients and we evaluated the possible correlation between VOCs and the presence of CKD and its stage. We enrolled 68 CKD patients under conservative therapy and 54 healthy subjects. The analysis of the VOCs of the exhaled air of the enrolled subjects was performed by SIFT-MS. Among all the VOCs analyzed, the most relevant results by ROC curves were observed for TMA, acetone, ammonia and dimethyl sulfide. We found that a breath TMA concentration superior to 26 ppbv characterizes a 6.11 times greater risk of CKD, compared to subjects with lower levels. Moreover, we detected an increased concentration of acetone and ammonia in CKD patients compared to healthy subjects. We highlight the potential utility of SIFT-MS in CKD clinical management.Clinical trial registry: R.S. 15.19 of 6 February 2019.Entities:
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Year: 2022 PMID: 35729207 PMCID: PMC9428186 DOI: 10.1038/s41598-022-14152-7
Source DB: PubMed Journal: Sci Rep ISSN: 2045-2322 Impact factor: 4.996
Descriptive statistic of target compounds.
| Median (min–max) | CI 95% | Mean | SD | Asymmetry | Kurtosis | |
|---|---|---|---|---|---|---|
| Trimethylamine, ppbv | 30 (0–49) | 20.48–30.30 | 25.70 | 12.67 | − .553 | .165 |
| Acetone, ppbv | 525 (180–1100) | 438.52–594.07 | 514.25 | 209.55 | .539 | 1.003 |
| Ammonia, ppbv | 13,000 (300–34,000) | 10622.50–17251.29 | 13,740.74 | 8690.05 | .757 | .455 |
| Isoprene, ppbv | 85 (30–170) | 72.67–100.22 | 86.44 | 37.26 | .474 | − .309 |
| Acetonitrile, ppbv | 0 (0–26) | 0–4.76 | 1.89 | 6.83 | 3.45 | 10.69 |
| Acetic acid, ppbv | 0 (0–770) | 6.63–105.73 | 41.85 | 148.03 | 4.92 | 24.99 |
| Propanoic acid, ppbv | 0 (0–190) | 1.11–26.59 | 10.33 | 36.87 | 4.80 | 23.95 |
| Ethanol, ppbv | 0 (0–310) | 0–40.59 | 14.56 | 60.08 | 4.93 | 24.97 |
| Butanol, ppbv | 14 (0–26) | 7.82–14.48 | 11.22 | 8.92 | − .141 | − 1.346 |
| Acetaldehyde, ppbv | 0 (0–52) | 1.19–11.37 | 5.56 | 14.07 | 2.42 | 4.82 |
| Dimethyl sulfide, ppbv | 19 (8.6–51) | 19.63–28.59 | 23.98 | 12.63 | .859 | − .338 |
| Trimethylamine, ppbv | 17.5(0–44) | 9.92–25.17 | 16.92 | 14.20 | .565 | − .326 |
| Acetone, ppbv | 405 (200–580) | 296.67–424.98 | 354.17 | 121.17 | .894 | .246 |
| Ammonia, ppbv | 2900 (2400–6200) | 3450.42–4749.57 | 4066.67 | 1165.67 | .350 | − .686 |
| Isoprene, ppbv | 94 (36–150) | 71.08–104.41 | 87.33 | 30.71 | .308 | .471 |
| Acetonitrile, ppbv | 0 (0–31) | 1.87–14.33 | 6.83 | 12.50 | 1.41 | .104 |
| Acetic acid, ppbv | 0 (0–230) | 0–57.50 | 19.18 | 66.39 | 3.46 | 12.00 |
| Propanoic acid, ppbv | 0 (0–0) | 0–0 | 0 | 0 | 0 | 0 |
| Ethanol, ppbv | 0 (0–0) | 0–0 | 0 | 0 | 0 | 0 |
| Butanol, ppbv | 14.5 (0–26) | 6.75–17.91 | 12.58 | 10.29 | − .204 | − 1.64 |
| Acetaldehyde, ppbv | 5 (0–30) | 1.83–16.41 | 8.42 | 12.70 | .962 | − 1.08 |
| Dimethyl sulfide, ppbv | 13 (0–36) | 11.11–20.58 | 15.51 | 8.62 | .805 | 2.851 |
CI confidence interval; SD standard deviation.
Reagent and product ions for all volatile organic compounds analyzed.
| Analyte | MW | Reagent ion | Branching raito | Product ion | Product ion m/z |
|---|---|---|---|---|---|
| Acetic acid | 60 | H3O+ | 1.00 | C2H5O2+ | 61 |
| NO+ | 1.00 | C2H4O2∙NO+ | 90 | ||
| O2+ | 0.50 | C2H4O2+ | 60 | ||
| Propanoic acid | 74 | H3O+ | 0.90 | C3H7O2+ | 75 |
| NO+ | 0.70 | C3H6O2∙NO+ | 104 | ||
| O2+ | 0.80 | C3H6O2+ | 74 | ||
| Ethanol | 46 | H3O+ | 1.00 | C2H7O+ | 47 |
| NO+ | 1.00 | C2H5O+ | 45 | ||
| 1-butanol | 74 | H3O+ | 0.95 | C4H9+ | 57 |
| NO+ | 0.95 | C4H9O+ | 73 | ||
| O2+ | 0.8 | C2H8+ | 56 | ||
| Acetaldehyde | 44 | H3O+ | 1.00 | C2H5O+ | 45 |
| NO+ | 0.20 | C2H4O∙NO+ | 74 | ||
| NO+ | 0.80 | C2H3O+ | 43 | ||
| Acetone | 58 | H3O+ | 1.00 | C3H7O+ | 59 |
| NO+ | 1.00 | C3H6O∙NO+ | 88 | ||
| O2+ | 0.40 | C2H3O+ | 43 | ||
| Acetonitrile | 41 | H3O+ | 1.00 | C2H4N+ | 42 |
| Isoprene | 68 | H3O+ | 1.00 | C5H9+ | 69 |
| NO+ | 1.00 | C5H8+ | 68 | ||
| O2+ | 0.45 | C5H7+ | 67 | ||
| O2+ | 0.45 | C5H8+ | 68 |
MW molecular weight.
Figure 1ROC curves: AUC and p values of TMA (A), acetone (B), ammonia (C) and dimethyl sulfide (D). Abbreviations: AUC area under the curve; TMA trimethylamine.
Logistic regression test and more significant odds ratio among VOCs tested.
| VOCs | OR | |
|---|---|---|
| TMA | 6.11 | 0.017 |
| Acetaldehyde | 0.216 | 0.047 |
| Dimethyl sulfide | 38*108 | 0.999 |
OR odds ratio; TMA trimethylamine; VOCs volatile organic compounds.
Independent test with Pearson’s correlation.
| Trimethylamine | Acetone | Ammonia | Dimethyl sulfide | ||
|---|---|---|---|---|---|
| Trimethylamine | Pearson’s correlation | 1 | .812** | .250* | .119 |
| Sign. (two codes) | .000 | .040 | .335 | ||
| N | 68 | 68 | 68 | 68 | |
| Acetone | Pearson’s correlation | .812** | 1 | .116 | -.025 |
| Sign. (two codes) | .000 | .348 | .837 | ||
| N | 68 | 68 | 68 | 68 | |
| Ammonia | Pearson’s correlation | .250* | .116 | 1 | .400** |
| Sign. (two codes) | .040 | .348 | .001 | ||
| N | 68 | 68 | 68 | 68 | |
| Dimethyl sulfide | Pearson’s correlation | .119 | .025 | .400** | 1 |
| Sign. (two codes) | .335 | .837 | .001 | ||
| N | 68 | 68 | 68 | 68 |
**The correlation is significative at level 0, 01 (two codes).
*The correlation is significative at levels 0, 05 and 0, 01 (a two codes).
Bonferroni-Holm correction.
| Compounds | Area under the curve ± SD | Minimal hypothesis | Close testing |
|---|---|---|---|
| Trimethylamine | 0.687 ± 0.07 | 0.0110 | 0.022 |
| Acetone | 0.648 ± 0.07 | 0.0450 | n.s |
| Ammonia | 0.902 ± 0.037 | 0.0001 | 0.0001 |
| Dimethyl sulfide | 0.740 ± 0.06 | 0.0451 | n.s |
n.s. not significant; SD standard deviation.
Figure 2Utility of SIFT-MS in the evaluation of VOCS in the exhaled air of CKD patients. Abbreviations: CKD chronic kidney disease; SIFT-MS selected ion flow tube-mass spectrometry; VOCs volatile organic compounds.
Figure 3VOCs sample collection of the exhaled air with SIFT-MS technique.
Epidemiological features and homogeneity of the two study populations.
| CKD patients | Healthy subjects | ||
|---|---|---|---|
| N | 68 | 54 | |
| Age (years) | 67.3 ± 10.1 | 63.2 ± 11.6 | Ns |
| Gender (M/F) | 37/31 | 29/25 | Ns |
| BMI (kg/m2) | 26.9 ± 3.9 | 27.6 ± 3.7 | Ns |
| Smokers (%) | 16.1% | 12.9% | Ns |